2012
DOI: 10.1007/s11258-012-0085-6
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Effects of elevated nitrogen and exotic plant invasion on soil seed bank composition in Joshua Tree National Park

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Cited by 34 publications
(28 citation statements)
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“…Cover and flowering of the other species was not affected significantly by 35N or 140N treatment (GLM; P40.1 in all the cases). Although exotic species in the seed bank can increase after N deposition 11 , we did not record any weeds or invasive species in the soil, which is consistent with the aboveground vegetation responses 5 .…”
Section: Resultssupporting
confidence: 85%
See 1 more Smart Citation
“…Cover and flowering of the other species was not affected significantly by 35N or 140N treatment (GLM; P40.1 in all the cases). Although exotic species in the seed bank can increase after N deposition 11 , we did not record any weeds or invasive species in the soil, which is consistent with the aboveground vegetation responses 5 .…”
Section: Resultssupporting
confidence: 85%
“…Despite widespread evidence of impacts of N pollution on floristic diversity and plant community structure 4,5 , studies on soil seed banks are scarce [10][11][12][13] and most are limited to short-term effects. For example, a 3-year study of N addition in a desert community found no change in the density or species richness of the seed bank 11 , while another 1-year study found that N addition increased seedling emergence 12 . One long-term study of N addition showed changes in seed bank composition in a tundra plant community 13 .…”
mentioning
confidence: 99%
“…A mix of these exotic species was planted at a total rate of 1600 live seed/m 2 . This seeding density is at the low end for naturalized annual grassland reseeding rates in the field (Dyer and Rice 1997, Hamilton et al 1999, Eviner and Firestone 2007, Schneider and Allen 2012, but was more than sufficient to create stands that achieved 100% aerial cover in the first year. All exotic grass seed was donated by Pacific Coast Seed (Livermore, California, USA).…”
Section: Experimental Design and Monitoringmentioning
confidence: 99%
“…Determining critical N deposition loads on specific habitats must combine manipulation experiments mimicking the frequency and temporal nature of the dry and wet N deposition at levels low enough to include the range of known N deposition, with observations on biodiversity, ecosystem processes and indicator species along anthropogenic N deposition gradients (e.g., Bobbink et al, 2010). Many manipulation experiments have been conducted to study potential impacts of N addition on ecosystems such as temperate grasslands (e.g., Morecroft et al, 1994;Horswill et al, 2008), Mediterranean shrublands (e.g., Vourlitis et al, 2009;Dias et al, 2011), deserts (e.g., Allen et al, 2009;Schneider and Allen, 2012), and the boreal tundra (e.g., Nemergut et al, 2008;DeLuca et al, 2007). However, the approach has some drawbacks, such as the limited number of years that it is practical to maintain such experiments (Duprè et al, 2010).…”
Section: Introductionmentioning
confidence: 99%